Jeong Hoon Byeon1. 1. School of Mechanical Engineering, Yeungnam University, Gyeongsan 38541, Republic of Korea.
Abstract
Ag-TiO2@polyethylene glycol (PEG) nanoparticles were continuously obtained in a single-pass configuration by appropriately reacting freshly flame-synthesized TiO2 with Ag formed in an ultrasonic aqueous medium containing PEG. When the proposed synthesis was kept constant, the production rate for Ag-TiO2@PEG nanoparticles reached approximately 3 g/h while only using a combination of a lab-scale inverse-diffusion flame (16 mm head diameter) and an ultrasonic Ag(I) cell (50 mL). The synthesized nanoparticles were employed as inducers for in vitro photoinduced therapy to kill cancer cells at different light wavelengths. Measurements of the nanoparticle cytotoxicity revealed that PEG incorporation with the Ag-TiO2 particles significantly decreased the cytotoxicity (cell viability of more than ~91% at 200 μg mL(-1) particle concentration) of Ag, and this was comparable with that of TiO2 particles (cell viability of more than ~90%). When 632 nm and 808 nm light was applied to the nanoparticles in the HeLa cells, the viability of the cells was significantly affected [decreased to ~4% (632 nm) and ~26% (808 nm) at 200 μg mL(-1), 5 min irradiation time] by surface plasmon resonance heating and photothermal therapy.
Ag-TiO2@polyethylene glycol (PEG) nanoparticles were continuously obtained in a single-pass configuration by appropriately reacting freshly flame-synthesized TiO2 with Ag formed in an ultrasonic aqueous medium containing PEG. When the proposed synthesis was kept constant, the production rate for Ag-TiO2@PEG nanoparticles reached approximately 3 g/h while only using a combination of a lab-scale inverse-diffusion flame (16 mm head diameter) and an ultrasonic Ag(I) cell (50 mL). The synthesized nanoparticles were employed as inducers for in vitro photoinduced therapy to kill cancer cells at different light wavelengths. Measurements of the nanoparticle cytotoxicity revealed that PEG incorporation with the Ag-TiO2 particles significantly decreased the cytotoxicity (cell viability of more than ~91% at 200 μg mL(-1) particle concentration) of Ag, and this was comparable with that of TiO2 particles (cell viability of more than ~90%). When 632 nm and 808 nm light was applied to the nanoparticles in the HeLa cells, the viability of the cells was significantly affected [decreased to ~4% (632 nm) and ~26% (808 nm) at 200 μg mL(-1), 5 min irradiation time] by surface plasmon resonance heating and photothermal therapy.
Strategic incorporation between isomers may help enhance composite nanoplatforms, which
can provide multi-functionalities in specific technological areas that are difficult to
achieve with one-component nanoparticles. Therefore, it is important to develop improved
metallic nanoparticles containing composite materials. In particular, there is an
increasing interest in developing biocompatible functional materials for metallic
nanoparticle technology, with an aim to combine the relevant properties of metals with
the peculiar performance of biomaterials1. However, currently available
metallic nanoparticles usually have poor compatibility with organic components, and it
is therefore rather difficult to homogeneously incorporate them into an organic matrix.
This limits the extension of their use in biomedical applications.Numerous approaches have been proposed for fabricating multifunctional biocompatible
nanomaterials that consist of inorganic-organic nanocomponents for application in
diagnostic and therapeutic fields. These nanomaterials usually contain metallic
nanoparticles as the core components with biofunctional polymers that endow the
nanomaterial with unique physicochemical properties for diagnostic and therapeutic
purposes234. Many formulations based on wet chemistry introduced
as suspension of solid particles have been proposed for biomedical applications, and
these may only be workable with desired performance in a short period of time5. Moreover, organic or polymeric components incorporated with metallic
nanoparticles are normally unstable owing to gradual degradation by hydrolysis;
biofunctional nanomaterials in a suspension or colloidal form would therefore not be
recommended. As a result, there is a need for a paradigm shift in the strategy for
preparing stable organic-inorganic hybrid nanomaterials with simpler and more versatile
processing for efficient use in biomedical applications6. Gas-phase
processing is an alternative method for preparing such nanomaterials with fewer
preparation steps, and it could allow long-term storage of the prepared nanomaterials in
a powder form7. Employing gas-phase processing further enhances the
process continuity in production, and this implies that only simple mechanical
collection of materials is required and large amounts of waste are not generated.
Moreover, employing wet chemistry approaches has been recently shown to achieve better
selectivity and safety in hazardous chemical processes and to exhibit many advantages
over conventional batch chemical processes3.Flame synthesis, which is one of the most promising gas-phase routes, has been utilized
for preparing a wide range of mono- and multicomponent functional nanoparticles with low
cost and high yield in commercial quantities1, and it could be scaled up
to a production rate of several hundred grams per hour without significant change in
material property8. However, conventional flame synthesis of functional
nanoparticles is commonly performed in high temperature conditions (over
1,700 °C). Since temperatures over
300 °C can decompose most organic materials (i.e. biofunctional
soft materials), the use of conventional flame synthesis would be only feasible to
synthesize hard or inorganic nanoparticles9. Thus, for producing
inorganic parts for hybrid nanomaterials is a single-pass configuration, flame pyrolysis
would not be suitable without the need for post-treatment or post-functionalization
steps; hence, this technique is still limited with respect to its use in a wide range of
biomedical applications10. Nevertheless, more recently, flame-synthesized
nanoparticles have often been employed as active materials for biomedical applications
via successive incorporation with biocompatible overlayers in a continuous manner1611. However, since this technique works only for inorganic
biomaterials, its application is still limited for generalized use. There have been
several studies on biomedical applications using metallic core-polymer shell
nanocomposites that exhibit high absorption at wavelengths longer than that of visible
light. Even though there are previous reports regarding organic matter/polymer
incorporation with flame-synthesized nanoparticles1213, it is still
desirable to conceive of simple, continuous, and efficient methodologies for biomedical
applications of flame-synthesized nanoparticles.This work introduces the potential use of Ag-TiO2@polyethylene
glycol (PEG) nanoparticles as photoinducers for killing cancer cells via flame-based
gas-liquid-gas single-pass processing. The flame-synthesized TiO2
nanoparticles were employed as a biocompatible support14 to produce
Ag-TiO2 nanobunches in order to enhance photoinduced cancer cell killing
by exploiting localized surface plasmon resonance including photocatalytic activity15. To functionalize the flame-synthesized TiO2 particles with
organic components in a continuous manner, an ultrasound Ag(I)-PEG reaction cell is
employed both for efficient hydrosolization of the TiO2 particles and for
subsequent incorporation with Ag and PEG on the TiO2 domains (Fig. 1). PEG is employed as overlayers for the Ag-TiO2
nanoparticles since it is known to be nontoxic to mammalian cells (i.e. biocompatible)
and non-antigenic16, which may also help it bond with metallic ions17.
Figure 1
Schematic of gas-liquid hybrid route for continuous fabrication of
Ag-TiO2@PEG nanoplaforms with a burner, Ag-PEG
solution reactor, and electrohydrodynamic atomizer connected in series.
Results and Discussion
To understand the formation of the Ag-TiO2@PEG nanocomposites
through the proposed hybrid processing, the samples electrostatically deposited as
TiO2, Ag@PEG, and Ag-TiO2@PEG
[(using a commercial particle collector (NPC-10, HCT, Korea)] directly on
carbon-coated copper grids in the gas-phase were analyzed using a transmission
electron microscope (TEM, JEM-3010, JEOL, Japan). The gas-phase sampling flow rate
was of 1.0 L min−1 in the collector. As shown
in Fig. 2a, the primary TiO2 particles
(~28 nm lateral dimension) were agglomerated, implying that
the primary particles collided with each other after they formed near the flame. As
seen in the inset of Fig. 2a, a lattice spacing of
approximately 0.35 nm was most frequently observed, which could be
matched to the (101) plane of anatase TiO218. In Fig. 2b (Ag@PEG sample), a darker contrast of
spherical particles exhibits the Miller plane (111) owing to a 0.24 nm
face-centered cubic (fcc) Ag lattice (inset), whereas lighter-contrast overlayers on
the spherical particles are attributable to the PEG. Thus, it was clearly observed
that ultrasonically formed Ag (from Ag+ to Ag0)
particles (8.8 ± 1.7 nm lateral
dimension) could be successively incorporated with PEG via successive reaction and
electrospray processes. In the case of Ag-TiO2@PEG, as shown
in Fig. 2c, the different particles (different size and
gradation) are combined as a single agglomerate, and it was clearly observed that
darker dots (because of Ag’s higher density than TiO2) were
randomly located on the TiO2 domains, which confirmed that the
Ag-TiO2 hybrid structures were successfully assembled. The lattice
spacing of the darker dots was ~0.24 nm corresponding to the
Miller plane (111) of Ag, while that of the lighter-contrast dots was
~0.35 nm corresponding to the (101) plane of
TiO2, implying coupling between distinct phase domains. The corresponding
fast Fourier transform images are also attributable to the fcc Ag and anatase
TiO2, respectively (Fig. 2d). As further
evidence, the X-ray diffraction (XRD, RINT-2100, Rigaku, Japan) analysis of the
TiO2 and Ag-TiO2 particles revealed that Ag particles
formed in the aqueous solution collided with incoming TiO2 particles
(Supplementary Fig. S1a). This
implies that the process enables incorporation of Ag particles at several sites on
the continuously incoming TiO2 particles. Furthermore, the Ag
agglomerates (shown in Fig. 2b) were redistributed on the
TiO2 domains due to deagglomeration (Eq. S1, Supplementary Information, by setting the
mechanical force from a pressure drop on an agglomerate of certain size owing to the
remarkable changes in pressure between the both sides of a nozzle for the
electrospray). When the agglomerated Ag@PEG passes through the nozzle,
it undergoes significant changes in mechanical conditions such as pressure and
velocity across the nozzle which induce a structural change of the
Ag@PEG before entering the nozzle. Figure 2c also
displays the incorporation of PEG on Ag-TiO2 particles, which may have
originated both from the Ag-PEG binding during Ag formation (Eq S2, Supplementary Information) in the
ultrasound reaction cell and from adsorptive incorporation during electrospray. To
confirm the latter, adsorption isotherms (Supplementary Fig. S2) were measured using the Micromeritics ASAP 2010
apparatus. A difference in the pore size distribution (inset) also supports the PEG
incorporation, which shows a significant decrease in the pore volume at meso- and
macro-porous regions after the PEG incorporation, implying that this adsorptive
property also might enhance the PEG incorporation on the Ag-TiO2
particles19. Figure 2d shows the energy
dispersive X-ray (EDX, JED-2300, JEOL, Japan) spectrum for the
Ag-TiO2@PEG sample. The low- and high-magnification scanning
electron microscopy (SEM, JSM-6500F, JEOL, Japan) images and the EDX spectrum peaks
correspond to Ag, Ti and O, and arrows in the high-magnification image indicate the
positions of Ag, Ti, and O in the sample. The weight fraction of Ag in the
Ag-TiO2 was ~40.1% in the present work, and this further
confirmed the Ag incorporation on TiO2 domains. When the system operation
is kept constant, the production rate for Ag-TiO2@PEG
particles reached approximately 3 g/h, and scale-up of this system may
achieve higher production rates (from kilograms to tons per day).
Figure 2
Low- and high-magnification electron microscope images to verify the
morphologies of the synthesized particles: (a) flame-synthesized
TiO2 nanoparticles; (b) ultrasound-assisted polyol
synthesized-electrosprayed Ag@PEG nanoparticles; (c)
ultrasound-assisted-electrosprayed Ag-TiO2@PEG
nanoparticles; and (d) SEM images and corresponding EDX profile, and
FFT image for Ag-TiO2@PEG nanoparticles.
The formation of Ag-TiO2 particles was also verified by means of UV-vis
absorption spectroscopy (330, Perkin-Elmer, US, Supplementary Fig. S3a). This is also attributed
to the dispersity of the Ag particles on the TiO2 domains by the
ultrasonic Ag(I) reduction and this induces an enhancement in the Ag particle
dispersity owing to increased interaction between the Ag and TiO2
particles, resulting in a broadening of the absorption. The inset of Supplementary Fig. S3a shows the X-ray
photoelectron spectroscopy (XPS, AXIS HIS, Kratos Analytical, Japan) spectrum of the
Ag-TiO2 nanoparticles. The characteristic peaks at
458.1 eV and 463.7 eV shown in Supplementary Fig. S1b are attributable to Ti
2p3/2 and Ti 2p1/2, respectively. There are
two more characteristic peaks at 367.5 eV and 373.5 eV in
Supplementary Fig. S1b, which are
attributable to Ag 3d5/2 and Ag 3d3/2,
respectively, proving the existence of a metallic Ag. Supplementary Fig. S3b displays Fourier transform
infrared spectra (FTIR, IFS 66/S, Bruker Optics, Germany) of the TiO2,
Ag@PEG, and Ag-TiO2@PEG samples. The bands around
1,270 and 1,005 cm−1 for the
Ag@PEG and Ag-TiO2@PEG samples may have arisen
from C-O, C-O-C stretches, and C-O-H bendings vibrations of the Ag particles in the
PEG matrix20.Flame-synthesized TiO2 particles were successively injected into an
aqueous Ag(I)-PEG solution in the presence of ultrasound to achieve bubble implosion
for efficient collection. To verify the quantitative collection of TiO2
particles, we measured the size distributions both in the absence and the presence
of ultrasound application. Most incoming TiO2 particles were trapped
(~98.5% efficiency) in the aqueous solution during ultrasound
irradiation. This may be due to bubble implosion before they reach the surface of
the solution, resulting in hydrosolization of nearly all TiO2 particles.
The particle size distribution was analyzed using a scanning mobility particle sizer
(SMPS, 3936, TSI, USA) to verify the number concentration, mean diameter, and
standard deviation of the electrosprayed Ag-TiO2@PEG
particles. The measured concentration, diameter, and deviation were
7.09 × 106 particles
cm−3, 125.0 nm, and 1.95, respectively,
as shown in Fig. 3. The same data for TiO2
particles are 3.05 × 106
particles cm−3, 61.1 nm, and 1.84,
respectively, and for the atomized Ag@PEG particles are
5.32 × 106 particles
cm−3, 115.8 nm, and 1.97, respectively.
The data for the Ag-TiO2@PEG particles were closer to that
for the Ag@PEG particles compared to that of the TiO2
particles. There was no additional peak and only an apparent increase in
concentration, not in size, suggesting that the TiO2 particles were well
merged with the Ag particles and thus forming Ag-TiO2@PEG
nanoparticles. In addition, the mass fractions of Ag, TiO2, and PEG in
the Ag-TiO2@PEG nanoparticle were measured using a
piezobalance particle monitor (3522, Kanomax, Japan) to be 0.38, 0.46, and 0.16,
respectively.
Figure 3
Particle size distributions of azerosol TiO2, Ag@PEG,
and Ag-TiO2@PEG nanoparticles.
We tested the cytotoxicity of the TiO2, Ag-TiO2, and
Ag-TiO2@PEG nanoparticles. In the case of
Ag-TiO2, a part of the dispersion was placed on HeLa cells to compare
the cytotoxicity among the samples. The MTT
[3-(4,5-dimethylthiazol-2-yl)-diphenyltetrazolium bromide] assay was employed to
evaluate cell viability by using incubation cells with samples for 24 h
(Fig. 4a). Measurements of cell viability showed that the
TiO2 nanoparticles had a cell viability of ~90% at
200 μg mL−1, which indicates
biocompatibility21, whereas the measured viabilities of the Ag
and Ag-TiO2 nanoparticles were significantly lower than that for the
TiO2 nanoparticles. The higher cytotoxicities for the Ag and
Ag-TiO2 particles may be due to the release of Ag ions in water from
the Ag particles (8.8 nm), and the released fraction of Ag ions reached
approximately 38.4 wt% (using inductively coupled plasma optical
emission spectrometry, Optima 8300, PerkinElmer, USA), which is consistent with a
previous report (4~9 nm, Ag particle size)22.
Analogous data for Ag-TiO2@PEG nanoparticles has the highest
cell viability, i.e. ~92% at 200 μg
mL−1. Although Ag-TiO2 nanoparticles
released the metallic component to clearly contribute toward cytotoxicity, the
released fraction of the PEG incorporated particles were not affected significantly
because of the biocompatible organic overlayers, as shown in Fig.
2c. This tendency is consistent with a previous report, which described
that protective PEG overlayers could decrease the cytotoxicity of nanoparticles to
mammalian cells2324. This suggests that the
Ag-TiO2@PEG nanoparticles from the successive Ag-PEG
incorporation of flame-synthesized TiO2 particles warrant further
investigation for their usage as photoinducers for HeLa cell killing. The zeta
potential of Ag-TiO2@PEG nanoparticles was
+2.2 mV at pH 7.4, and this value was relatively more positive than that
for the PEG-capped Ag particles prepared by wet chemistry25, hence
this may provide higher affinity with negatively charged biological membranes.
According to a common protocol for testing the photothermal activity of
Ag-TiO2@PEG nanoparticles, we first measured the
temperatures of the media in the presence of light irradiation for a duration of
5 min. The nanoparticle solution embedded in agar was exposed to laser
of wavelength 632 nm or 808 nm (2.15 W
cm−2). These wavelengths were chosen since they are
within the absorption range of the Ag-TiO2 nanoparticles (Supplementary Fig. S3a). The absorption spectra of
Ag-TiO2 particles showed a significant shift towards the longer
wavelength (480~650 nm) compared with TiO2
particles, which is comparable with results from a previous report26.
The broadened and shifted spectra may be due to the surface plasmons of Ag particles
that depend on the morphology (i.e., nanobunches) and surrounding environment. The
red shift in the spectra may have resulted from the interaction between Ag and
TiO2 particles, where the Ag particles were deposited on the
TiO2 surface27. The temperature, which was measured
using an IR thermometer with a thermal camera (Supplementary Fig. S4), increased with an increase in laser irradiation
time, and the local temperature reached 51.5 °C. Hence, the
maximum values (23.1 °C at 632 nm and
16.3 °C at 808 nm) of ∆T
(Eq S3, Supplementary Information)
could be realized at 200 μg mL−1
of mass concentration, while the analogous value for the 365 nm
wavelength was 0.2 °C. From the temperature measurements, it
can be concluded that the Ag-TiO2 nanoparticles absorbed the irradiated
laser light, and the light was successively converted into thermal energy. Based on
this photothermal conversion of the Ag-TiO2 particles upon
632 nm or 808 nm excitation, in vitro photothermal
therapy using Ag-TiO2@PEG nanoparticles was investigated. To
measure the photothermal activity of the nanoparticles for cell killing (Fig. 4b), adenosine triphosphate (ATP) assay was employed. The
thermal energy obstructed the ATP production of the cells owing to the heat when the
laser irradiated the culture medium. According to previous reports282930, the positive effect of temperature on photoinduced
reactions in the presence of plasmonic and nonplasmonic noble metal nanoparticles is
interpreted in terms of the redistribution of the metal electron into higher energy
levels and the increase in vibrationally excited states with increasing temperature.
Thus, the cell viability significantly decreased from thermo/chemical reactions with
the embedded nanoparticles. Live or dead cells were differentiated by calcein AM
(live cells, green fluorescence, Life Technologies, USA) and propidium iodide (dead
cells, red fluorescence, Life Technologies, USA) after laser irradiation (inset of
Fig. 4b). In the control group
(Ag-TiO2@PEG nanoparticles only), nearly all cells displayed
green fluorescence, so the particles themselves have no significant cytotoxic
effects. When the nanoparticles are exposed to laser with different wavelengths, the
particles show a photothermal effect on HeLa cells; hence, only cells within the
laser spot were killed, showing homogeneous red fluorescence. The cells outside the
region of the spot were mostly kept alive, showing green fluorescence. In
particular, when the concentration is 90 μg
mL−1, the viability of the cells incubated with
Ag-TiO2@PEG nanoparticles decreased significantly with
irradiation (2.15 W cm−2), and more than 80%
of the cells were killed within 5 min of irradiation
(632 nm). This performance is comparable with that in a previous
report31 where modified TiO2 nanoparticles were
employed with 5 min of irradiation (2.00 W
cm−2). Even though there is a difference in the
maximum temperature between the current and previous results for 5 min
of laser irradiation, both results reveal temperatures over
50 °C that can easily kill cancer cells32.
This implies that the proposed approach has feasibility that may be investigated
further. In addition, the analogous result for the 365-nm wavelength did not show
significant enhancement (more than ~80% in cell viability even at
200 μg mL−1) in cell killing,
implying that the produced heat was rather critical for the cytotoxic effect. The
weaker performance at the UV case may be due to significant UV absorption
(~70% for <400 nm wavelength) by a silicon-coated
polyethylene terephthalate (PET, 125-μm thickness, Loparex, USA)
film33 that was employed to simulate the laser irradiation on
skin3435.
Figure 4
Biological analyses regarding photothermal activity of
Ag-TiO2@PEG nanoparticles: (a) cytotoxicity of
TiO2, Ag, Ag-TiO2 and
Ag-TiO2@PEG nanoparticles; and (b)
photothermal activity for killing HeLa cells upon irradiation with different
wavelengths.
Furthermore, another scenario for parenteral applications was considered, where the
Ag-TiO2@PEG nanoparticles are administered to tissues
that attract activated macrophages. In order to suppress inflammatory responses,
nanoparticle interaction with biological system has recently been studied for
biofunctional nanoparticulate systems36. The results (Fig. 5) show that the Ag-TiO2@PEG nanoparticles
could more significantly suppress the macrophage inflammatory protein (MIP)
production from lipopolysaccharide (LPS)-challenged macrophages than those from
polyethyleneimine (PEI) or poly-l-lysine (PLL) [as well as phosphate buffered saline
(PBS)] incorporated Ag-TiO2 nanoparticles (insets of Fig.
5). The smaller MIP productions of the Ag-TiO2@PEG
nanoparticles than that from the PEI or PLL incorporated particles indicate that the
tendency may be related to the amine content (i.e., no amine groups in PEG).
Figure 5
MIP production from LPS-challenged macrophages by adding PEI, PLL, and PEG
incorporated
(2 × 10−6 mol
dm−3) Ag-TiO2 nanoparticles.
Insets show representative TEM images (scale bar, 50 nm) of the
polymer incorporated Janus particles.
A continuous aqueous Ag-PEG capping of flame-synthesized TiO2
nanoparticles via gas-liquid hybrid processing was employed for the first time for
scalable production of inorganic-organic nanoplatforms. The fabricated nanoplatforms
were directly employed to evaluate their biocompatibility and photothermal activity
for killing cancer cells. A further study to optimize the proposed method for
realistic applications regarding modulation of optical property and cytotoxicity is
now in preparation for publication elsewhere. This strategy could allow on-demand
fabrication of fresh biomaterials for use in biomedical applications, and may also
hold immense promise in biomaterial coatings. These results further establish
continuous hybrid processing as an efficient, green, and scalable design and
fabrication methodology, which is generalizable to a wide range of therapeutic and
diagnostic agents for both biomedical and scientific purposes.
Materials and Methods
Nanoparticles synthesized in the gas-phase can be suspended into a liquid for
coupling to wet-chemistry routes, thus enabling development of other innovative
methods for novel material synthesis373839. When incorporating
metal in a liquid state, hydrated electrons produced during mixing and heating could
reduce metal ions to metal particles of zero valences. In the present work, the
flame-synthesized TiO2 inorganic particles were injected into an
Ag(I)-PEG containing aqueous solution in the presence of ultrasound for capping of
the TiO2 particles with newly formed Ag-PEG (Fig.
1). The TiO2 particles were ultrasonically trapped in the solution
when the ultrasound reached the bubbles containing TiO2 particles in the
solution. When solutions containing AgNO3 and PEG were separately
injected into the reactor containing TiO2 particles, the Ag ions would
reduce and subsequently deposit on the trapped TiO2 particle by
ultrasound-assisted reaction and mixing. They were then aerosolized via electrospray
to fabricate nanoscale PEG incorporated Ag-TiO2 photoinducers, and
finally employed to kill humanepithelial carcinoma (HeLa, ECACC No. 93021013) cells
upon light irradiation (with a 632 nm or 808 nm wavelength,
VA-I-DC, Rhysics Phototronics, Korea).Specifically, as shown in Fig. 1, a commercial co-flow quartz
burner (141/18/60, Arnold Gruppe, Germany) equipped with a bubbler was employed to
produce TiO2 nanoparticles. The H2 (fuel) intake is made
through 4 capillaries, and the TiCl4 precursor (208566, Sigma-Aldrich,
USA) was fed to the flame via bubbling air passing around the 4 capillaries after
mixing with another air acting as oxidant and sheathing gas. The H2 flow
rate was 1.2 L min−1, and the air flow rates
for bubbling and oxidation were 0.3 and 6.0 L
min−1, respectively. The flow rates were separately
controlled with mass flow controller (Tylan, USA). The synthesized TiO2
particles passed through the tube furnace containing silica gel and activated carbon
pellets to remove extracted solvent and were driven to a conical chimney, which
directly drove the part of particles using a vacuum transducer pump into the
ultrasonic the Ag(I) cell containing PEG to employ as domains for synthesizing
Ag-TiO2 nanoparticles in Ag(I)-PEG solution. In the reaction cell,
solutions 1 and 2 were injected with the aid of a peristaltic pump (323Du/MC4,
Watson-Marlow Bredel Pump, USA) at constant rates of 0.42 and 2.08 mL
min−1, respectively. 85 milligrams of
AgNO3 (205052, Sigma-Aldrich, USA), used as a precursor of Ag, was
dissolved in 5 mL of deionized water (Solution 1). 0.2 grams
of PEG (81253, Sigma-Aldrich, USA), used both as a reducing agent and a stabilizing
agent, dissolved in 25 mL of distilled water (Solution 2). An ultrasound
probe (VCX 750, 20 kHz, Sonics & Materials Inc., USA) was
immersed into the solution. The probe acted as an ultrasound irradiator
(10 W mL−1 input power density) and the
active part of the probe was the planar circular surface, of area
1.3 cm2, at the bottom of the probe. Upon the start
of reactions, the pale yellow solution changed to light brown indicating the
reduction of Ag(I).The Ag-TiO2@PEG suspension was aerosolized via electrospray,
by means of the equipment assembled in-house. In brief, the equipment consisted of
another peristaltic pump (07522-30, Masterflex, USA), a stainless-steel nozzle
(inner diameter 0.3 mm), a high-voltage power supply (10/40A, Trek,
USA), and a stainless steel plate placed directly below the nozzle as the grounded
count electrode at a distance of 40 mm between the capillary and the
substrate. The prepared solution was electrosprayed (16 μL
min−1) in a heated tube installed between a capillary
and a polytetrafluoroethylene substrate (66042, Satorius, Germany) using the pump
(3032, TSI, USA) to perform a deposition of Ag-TiO2@PEG
nanoparticles on the substrate. The detached nanoparticles from the substrate were
then employed to evaluate their cytotoxicity and photothermal activity upon light
irradiation.Synthesized Ag-TiO2@PEG nanoparticles were evenly dispersed in
2% agar (Invitrogen, USA) at concentrations of 20, 50, 90, 140, and
200 μg mL−1. The gels were formed
in shallow, 35 mm diameter plastic petri dishes. For exposure, the gel
phantom samples at room temperature were exposed to a photoirradiation system
passing through a silicon-coated PET film (to simulate the laser irradiation on
skin) with different wavelength ranges (365, 632, and 808 nm). The gel
samples were positioned in the light and irradiated by the beam (2.15 W
cm−2 irradiation intensity) for a fixed duration of
5 min. In order to evaluate the application to photothermal cell
killing, ATP assay (BioVision, USA) was employed, which is based on a highly
sensitive firefly reaction to determine the level of cellular ATP as a surrogate
marker for the number of live cells. After a 24 h incubation with
Ag-TiO2@PEG nanoparticles, the cells were washed three
times with a Hank buffered salt solution (H9394, Sigma-Aldrich, USA), and
0.1 mL of CellTiter-Glo Luminescent (Promega, USA) assay reagent was
added to each well, and the plate was then mixed using an orbital shaker for
2 min, followed by 10 min incubation to stabilize the
luminescence signals. Luminescence was read using a luminometer (GloMax 20/20,
Promega, USA).Peritoneal macrophages (ATCC CRL-2457) were seeded in 24-well plates at a density of
105 cells per well in 1 mL of medium. After overnight
incubation, 0.1 mL of the Ag-TiO2@PEG
nanoparticle solution was injected to each well to set the particle concentration in
medium to 2 mg mL−1. For comparison purposes,
0.1 mL of polyethyleneimine (PEI, 765090, Sigma-Aldrich, USA),
poly-l-lysine (PLL, P4707, Sigma-Aldrich, USA), or PEG was injected in lieu of the
Ag-TiO2@PEG nanoparticle solutions. After
24 h incubation, the culture media were centrifuged at
2000 rpm for 10 min to separate supernatants. Macrophages
were challenged by adding lipopolysaccharide (LPS) to the media in the final
concentration of 1 μg mL−1
shortly before the comparisons. Enzyme-linked immunosorbent assay (ELISA) was
performed to determine the MIP levels using MIP-2 ELISA kit (R&D Systems,
USA). The supernatants collected from LPS-challenged macrophages were always diluted
10 times prior to the analysis. The differences were considered significant for
p < 0.01.All experiments were performed in triplicate, and the results were reported as
average values and standard deviations.
Additional Information
How to cite this article: Byeon, J. H. Scalable hybrid chemical manufacture to
photothermal therapy: PEG-capped phototransducers. Sci. Rep.
6, 31351; doi: 10.1038/srep31351 (2016).
Authors: Rares Stiufiuc; Cristian Iacovita; Constantin M Lucaciu; Gabriela Stiufiuc; Alina G Dutu; Cristiana Braescu; Nicolae Leopold Journal: Nanoscale Res Lett Date: 2013-01-23 Impact factor: 4.703
Authors: David O Raemy; Robert N Grass; Wendelin J Stark; Christoph M Schumacher; Martin J D Clift; Peter Gehr; Barbara Rothen-Rutishauser Journal: Part Fibre Toxicol Date: 2012-08-17 Impact factor: 9.400